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Applied and Environmental Microbiology, September 1998, p. 3246-3255, Vol. 64, No. 9
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Rapid Determination of Bacterial Abundance, Biovolume,
Morphology, and Growth by Neural Network-Based Image
Analysis
Nicholas
Blackburn,1,*
Åke
Hagström,2,
Johan
Wikner,3
Rocio
Cuadros-Hansson,3 and
Peter Koefoed
Bjørnsen2
Marine Biological Laboratory, DK-3000
Helsingør,1 and
National Environmental
Research Institute, DK-4000 Roskilde,2 Denmark,
and
Umeå Marina Forskningscentrum, Norrbyn, S-910 20 Hörnefors, Sweden3
Received 20 November 1997/Accepted 27 May 1998
 |
ABSTRACT |
Annual bacterial plankton dynamics at several depths and locations
in the Baltic Sea were studied by image analysis. Individual bacteria
were classified by using an artificial neural network which also
effectively identified nonbacterial objects. Cell counts and
frequencies of dividing cells were determined, and the data obtained
agreed well with visual observations and previously published values.
Cell volumes were measured accurately by comparison with bead
standards. The survey included 690 images from a total of 138 samples.
Each image contained approximately 200 bacteria. The images were
analyzed automatically at a rate of 100 images per h. Bacterial
abundance exhibited coherent patterns with time and depth, and there
were distinct subsurface peaks in the summer months. Four distinct
morphological classes were resolved by the image analyzer, and the
dynamics of each could be visualized. The bacterial growth rates
estimated from frequencies of dividing cells were different from the
bacterial growth rates estimated by the thymidine incorporation method.
With minor modifications, the image analysis technique described here
can be used to analyze other planktonic classes.
 |
INTRODUCTION |
A standard procedure used to
determine concentrations and biovolumes of microorganisms in studies of
the population dynamics of natural aquatic communities is microscopic
examination of filtered fluorescently dyed cells (10, 14,
19). Counting and measuring individual cells are normally done
visually, which is tedious and time-consuming. It is possible to
automate the procedure as follows: (i) the microscope image is
digitized with a camera and digital frame grabber, (ii) the image
is processed to distinguish objects from the background, and
(iii) parameters and features of individual objects are analyzed.
For the most part these tasks have been studied individually by workers
in different disciplines. Complete automation of sample filtration and
microscope loading has not been achieved, but image analysis can be
fully automated simply and cheaply (17). Below, we describe
a combination of methods which can be used for versatile, efficient
processing of many images in order to obtain reliable, high-resolution
data on aquatic plankton dynamics, particularly the dynamics of the bacterial fraction. The 1995 annual dynamics of bacterial plankton samples obtained at three stations in the Gulf of Bothnia at multiple depths were used in this study for purposes of analysis and
illustration.
Camera and microscope.
Charged coupled device (CCD) cameras
are the best choice for photometric applications. However, the exposure
times under epifluorescence conditions at high magnifications are
around 1 s and thus are much longer than the maximum exposure time of
standard video cameras (1/25 s). Many manufacturers produce special
cameras which allow integration of light over long exposure times,
resulting in high image quality and low noise. Typically, these
cameras display images in standard video resolution (ca. 700 by
500 pixels) from a frame buffer. Their control boxes often have a
built-in frame grabber for transferring digital images to a computer.
There are economic advantages in being compatible with standard video
cameras, but the small image matrix limits the field of view and the
number of gray levels used to render the image (dynamic range) is
usually limited to 256. Cameras with larger image matrixes (e.g., 1,000 by 1,300 pixels) are available. These cameras are expensive but usually
offer a high dynamic range in addition to a large field of view. This
can be important for capturing faint details, such as flagella, without
overexposing cell bodies.
The resolution of an optical system can be defined as the ability to
discern spatial frequencies (25). The minimum distance (dres) between two lines that can be resolved at
a wavelength of
with a microscope objective having a numerical
aperture of N is (25):
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(1)
|
Full use of the resolution of the optics occurs when the pixel
size in the resulting digital image is less than
0.5dres. A typical setup is
= 0.5 µm and
N = 1.3, which results in 0.5dres = 0.048 µm. A CCD with a pixel size of 12 µm requires a magnification of
about ×250 (12 µm/0.048 µm) for maximum feature definition. In
practice, feature definition can be compromised for a larger field of
view by lowering the magnification somewhat.
Identification of objects.
The limited resolution of
microscope optics results in blurred edges of objects when they are
viewed at high magnification (see above). In addition, uneven lighting
and differences in exposure times and object luminescence make it
impossible to choose a single gray level as a threshold for
distinguishing objects from the background. Viles and Sieracki
(27) discussed this problem with respect to bacteria under
epifluorescence conditions and concluded that a Marr-Hildreth operator
(16) functions with a high degree of independence for
exposure and lighting characteristics and with accurate edge detection
properties. A Marr-Hildreth operator is a combination of a Gaussian
operator for smoothing and a Laplace operator for amplifying high
spatial frequencies. The Laplace operator calculates the second
derivative of intensity. If the edge of a blurred object is at the
point where the rate of intensity change is greatest (second
derivative), the Laplace operator identifies its position as the zero
crossing between positive and negative values. This seems logical and
is appealing, because it is suspected that basic animal vision
functions in somewhat the same way (16) and virtually the
whole problem of edge detection is solved with only two operations
(i.e., applying the Marr-Hildreth filter and thresholding to a constant
value). However, the Laplace operator is sensitive to electronic camera
noise (17) and to faint particles, which can be a problem
for analysis of, for example, soil smears (3).
Classification of objects.
Classification of objects has been
elegantly accomplished to a remarkable degree with animal vision, and
trying to mimic this process in machine vision is an obvious goal. One
tool which can be used for this is an artificial neural network. An
artificial neural network can be thought of as a complex function that
can be programmed to give a certain output configuration in response to
a certain input configuration. This is thought to be the means by which
true neural networks work in a nervous system, and the procedure of programming an artificial neural network is called "training." The ability of an artificial network to learn can be
measured by its ability to generalize beyond the examples that it is
given during the training procedure. The use of a network for
classification is attractive because the decision concerning which
components of the definition are most important for classification is
made automatically. In order for the network to perceive an object, it
must be supplied with a definition of shape. The raw image data
contains too many degrees of freedom for a simple definition. It is an
advantage to have a definition which has a constant number of
parameters in order to simplify the shape and which is rotation independent. The best way to accomplish this is to use the Fourier transform, which converts spatial data in the form of coordinate pairs
or intensity matrixes into spatial amplitudes, frequencies, and phases.
This separates information related to rotation, intricacy of detail,
and position. Simpson et al. (22) and Culverhouse et al.
(4) used a subset of the power spectrum of the
two-dimensional Fourier transform with binarized images to define
certain phytoplankton and protozoans. Svarer (26) used an
elliptic Fourier transform in which each pixel coordinate pair in the
object contour was a complex number. The two approaches are similar,
but the latter is faster, and the simplified shape of each object can
be reconstructed with the inverse transform and can be plotted to give
a view of how the network classifier perceives the object definition.
Contour definitions, however, have limitations. A more sophisticated
definition is required for species which are identified by color or
texture, but the approach could be considered the first step in a
multilevel procedure for achieving a good description. Sophisticated
staining procedures help segregate major classes into, for example,
DNA-containing organisms, heterotrophs, autotrophs, and detritus
(20, 28, 29), especially in conjunction with a bandpass
filter (27). Confocal microscopy can improve contrast and
resolution by eliminating light from objects which are out of focus,
and this technique works well with specific staining for highlighting
objects of interest (e.g., bacteria) (3).
Growth rates.
The frequency of dividing cells (FDC) in a
microbial community reflects the growth rate (12).
Frequencies corresponding to bacterial growth rates in situ are often
only a few percent, which makes the method particularly attractive when
a large number of individuals can be processed. It has been
demonstrated that accurate FDC measurements can be acquired by image
analysis (3).
 |
MATERIALS AND METHODS |
Samples and preparation.
In 1995, water samples were
collected in the Gulf of Bothnia as part of a Swedish national
environmental monitoring program. Samples were collected six times
(weeks 2, 20, 26, 32, 36, and 48) during the year at the following
three stations: F9 (subarctic, off-shore; 64°42.5'N, 22°04.0'E),
US5 (off-shore; 62°35.0'N, 19°58.5'E), and NB1 (coastal;
63°30.5'N, 19°48.0'E). Samples were obtained from five to nine
depths at each station. The samples were fixed in formalin and stored
at 5°C. The analysis was performed in September 1996. In order to
visualize bacteria, 4- to 10-ml samples were stained with acridine
orange and filtered onto black, 0.2-µm-pore-size Nuclepore filters
(14). The filters were then briefly allowed to dry at room
temperature, immersed in paraffin oil on microscope slides, and covered
with coverslips.
Image acquisition.
A Hamamatsu model C4742 black and white
digital camera (1,000 by 1,018 pixels; pixel size, 12 µm; 10-bit
dynamic range; 1,024 gray levels) was mounted on a Zeiss Axiovert 100 epifluorescence microscope equipped with a Plan Neofluar 100x/1.3 oil
immersion objective. The pixel size in the resulting image was 0.12 µm square. The exposure times were approximately 0.33 s. Images
were acquired from the camera with an Imagequest IQ-D100 digital frame
grabber (Hamamatsu) housed in a Power Macintosh 7100/66 computer. The frame grabber's application program, IQBase, was used to view images
on the computer screen for focusing, capturing, and saving to disc.
Care was taken to expose the CCD correctly, which kept all objects of
interest within the camera's dynamic range.
Image analysis.
Standard image analysis functions were
obtained from a library (IMAQ Vision) for the programming language
LabVIEW of National Instruments. LabVIEW is a high-level graphical
programming language with an integrated user interface that resembles
the front panel of an electronic instrument. Each image analysis
function (e.g., convolution, thresholding, object identification, etc.)
is a single icon in the graphical program diagram, so each icon
functions as a macro. The use of this programming tool allowed
efficient integration of all stages of image processing, object
classification, and database management and at the same time provided a
high degree of interactivity while the system was programmed to
automatically classify objects by using an artificial neural network.
The analysis procedure was implemented in two similar programs, an
interactive version (LabMicrobe) and a batch-processing version
(BatchMicrobe), available from DIMedia, Kvistgård, Denmark. LabMicrobe
was used to initially train an artificial neural network, and
BatchMicrobe was used to automatically process digitized images from
disc. Processing was performed with 16-bit precision to make full use of the 10-bit dynamic range of the camera.
The survey of annual bacterial plankton dynamics was based on samples
obtained from three stations at five to nine depths, on six occasions;
a total of 690 images were examined. Each image contained approximately
200 bacteria. Five images were analyzed per filtered sample, which
resulted in a standard error for counts of around 5%. Very little
variation in cell counts between filters was observed (<5%) with the
filtering procedure used.
Edge detection for identification of objects was performed with the
Marr-Hildreth operator; the results are shown Fig.
1B.
A rank 3 filter (every pixel in the
image was replaced by the
third-least-intense neighbor) was used to
remove pixels that had
intensities equivalent to the intensities of
amplified background
noise (
17) but were falsely associated
with the edges of objects,
resulting in the image shown in Fig.
1C.
Most of the background
noise was effectively removed with a threshold
of 2 (Fig.
1D),
which produced a binary image. Objects narrower than 2 pixels
were subsequently removed with a function from the IMAQ library
(based on erosion of the image), which resulted in the final binary
image used for measurement and classification (Fig.
1E).

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FIG. 1.
Edge detection procedure. The images in panels B and C
were binarized in order to visualize image structure, while
calculations were performed with nonbinarized images. (A)
Cutout of the original image. (B) Image after application of the
Marr-Hildreth operator with 3×3 kernel, thresholded to gray level 1 for contrast. (C) Image after application of a rank 3 filter. (D)
Binary image after thresholding to gray level 2. (E) Image after small
particles were removed by using an erosion algorithm.
When the results are compared with the original image, it must be
realized that the image was represented in 1,024 gray levels, whereas
the human eye can discern only approximately 100 gray levels.
Because of this, some of the objects detected were too faint to be
visible, and some bright objects were too small to be accepted.
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Comparisons of humans and machines.
The microscope setup
described above was also used for manual counting. Sample volumes that
resulted in at least 30 cells per field were used, and at least 20 fields were counted for each sample. If necessary, more fields were
checked to obtain a standard error of less than 5%. The brightness of
stained cells changes with time after fixation in formalin. This causes
problems, particularly for humans, who use intensity criteria to
determine what objects to count. In this study we used samples
collected in 1997 during the same monitoring program for the
comparisons so that relatively long storage times would not affect the
results; these samples were filtered within a few hours after
collection and were stored frozen.
Bacterial cell volumes.
The most accurate parameter measured
by an image analyzer is the projected area of an object (A),
because it is just the number of pixels that define the object. This
parameter was used together with the longest chord (used to estimate
length [l]) in order to calculate radius (r)
and volume (V) values, based on the observation that
bacteria are basically shaped like cylinders with hemispheric ends:
|
(2)
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|
(3)
|
To estimate the precision of measurements, slides containing
fluorescent latex microspheres (Polyscience Ltd.) having diameters
of
0.52 and 0.80 µm were prepared in the same way as the slides
containing bacteria, and the resulting images were processed with
LabMicrobe.
Object classification.
There were basically only two main
morphological classes of bacteria observed in significant numbers, rods
(class R) and crescent-shaped vibrios (class V). The rods were
subdivided into three classes based on elongation factors (length of
the longest chord/mean width). Cocci and short rods (class R1) had
elongation factors ranging from 1 to 3, short rods (class R2) had
elongation factors ranging from 3 to 6, and long rods (class R3) had
elongation factors ranging from 6 to 12. This classification was based
on the assumption that bacteria usually increase in length to
approximately twice the average length before they divide
(9). A total of 60 objects belonging to each main class
(classes R and V) were used as a training set, and 20 class R1 objects,
20 class R2 objects, and 20 class R3 objects were included to make sure
that classes R1, R2, and R3 were represented equally (Fig.
2). Sixty objects identified as
nonbacteria (class X) were also included (Fig. 2). The training set was
introduced into LabMicrobe in the binary image form, and objects
belonging to each class were pointed out to the program with the
computer's mouse prior to training. LabMicrobe traces the contours of
objects by using a simple algorithm implemented by us and calculates
the complex Fourier transform by using LabVIEW's built-in
signal-processing library. In this procedure, each complex number is
the coordinate pair of each pixel in the contour. In Fourier space,
contours were rendered independent of object position, rotation, and
start position of the sampling point for the contour as described by
Svarer (26). Shapes were subsequently simplified by using
the eight lower spatial frequencies and their eight corresponding amplitudes, which together described the main characteristics of shape
with the details (high frequencies) removed (Fig.
3). These 16 descriptors representing
contour definitions were used to train a network consisting of 16 input
nodes (one for each parameter), 5 intermediate nodes, and 3 output
nodes (one for each class). The network was trained by LabMicrobe in an
iterative process in which object definitions were chosen one by one at random and applied to the standard Back-Propagation algorithm (6) implemented by us for LabVIEW. The trained network was used by BatchMicrobe for the automatic classification procedure, using the Feed-Forward algorithm. A sigmoid activation function was
used:
|
(4)
|
where
x is the input at a given node in the network.
The network was trained to put out a high number (0.9) at the node
corresponding
to the input configuration's class and a low number
(0.1) at other
nodes. The network was saved after training and was
subsequently
used for classification. Classification of each object was
based
on the index of the output node having the highest value over
0.5. Classification was considered unsuccessful if no output node
registered a value of more than 0.5. About 95% of all objects
were
classified in each image.

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FIG. 2.
Entire training set used for the neural network
classifier. The objects represent the main classes, including rods
(classes R1, R2, and R3), vibrios (class V), and rejected objects
(class X). The objects were chosen manually and were copied from images
processed by the image analysis procedure described in the text.
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FIG. 3.
Levels of detail achieved by using different numbers of
Fourier coefficients (solid lines) for defining the contours of objects
(stippled lines). Sixteen coefficients were used for this study.
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Thymidine incorporation.
Bacterial biomass production as
determined by thimidine incorporation was studied by using the method
of Smith and Azam (23). [3H]thymidine was
added to a concentration of 25 nM. A thymidine conversion factor of
1018 cells/mol was used (2).
FDC.
Dividing cells were defined as cells that contained two
local intensity maxima. Such cells were detected by applying a filter which replaced each pixel in the image with the pixel having the maximum intensity in its neighborhood, including itself (Max), to the
original gray scale image (G), subtracting G,
thresholding to 1, and multiplying with the binary image (B)
obtained after edge detection. This resulted in a binary image
(D) with holes "punched" at the locations of local
intensity maxima:
|
(5)
|
Dividing cells were then identified as objects containing two
holes. This method resembled the method described by Bloem
et al.
(
3).
Statistics.
Data series were transformed by the natural
logarithm when appropriate to approach normality. Significance levels
in the analysis of variance were calculated by using the interaction
term and pooling as described by Sokal and Rohlf (24). The
statistical software SYSTAT was used.
Database management.
Parameters (i.e., cell volume,
elongation factor, number of holes, and class of each object) were
saved in a spreadsheet-formatted file for each image by BatchMicrobe.
These parameters were fed through a utility program written in LabVIEW
to segregate the data into classes based on classifications determined
by the neural network and elongation factors. A second utility program
was used to calculate cell volume histograms for each class. The
histograms were then imported to a spreadsheet for final calculations
and plotting.
 |
RESULTS AND DISCUSSION |
The strength of the image analysis method for performing
large-scale surveys lies in its speed and consistency. This in turn allows sampling at a higher resolution than is practical manually. While automatic filtration and slide loading are mechanical problems that await practical solutions, the automatic image analysis procedure is a major step toward completely automatic monitoring. The processing times for images (1,000 by 1,018 pixels) when the procedure described above was used were roughly proportional to the number of objects (about four objects per s or one image per min), and computers that are
many times faster than this are readily available. In this context,
field results were used mainly to demonstrate that the image analyzer
was able to identify interesting patterns of microbial activity in time
and space within its limited resolution and that it was as accurate as
a human in counting and measuring bacterial cells.
Object classification.
The most important task for the
classifier in this survey was to segregate cell-shaped objects from
other objects, such as detritus particles and particles created
artificially as a result of noise and filtering. Figure
4 shows how the members of a subset of
all of the objects from five images were classified by the machine.
With the resolution used, only a few percent of the objects were
classified incorrectly or were considered unsuccessfully classified.
There was generally excellent agreement between manual and machine
counts for samples collected in the summer months, but the machine
consistently estimated higher bacterial concentrations in samples
collected during the winter months (Fig.
5). An examination of individual
microscope fields revealed that the machine included cell-shaped
objects that fluoresced too faintly for the human counter to accept as
bacterial cells, but these objects would have been counted if they had
been brighter.

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FIG. 4.
All objects that were obtained from five images from a
sample collected at station US5 (week 32; depth, 8 m) and
contained exactly two well-defined local intensity maxima (white dots
surrounded by eight solid pixels). The presence of two well-defined
local intensity maxima was used as the criterion to identify dividing
cells. The image analyzer clearly classified these objects into correct
classes, and only a few objects were classified as unidentifiable (?
class). Only class R1 and R2 objects were used to obtain growth rate
estimates.
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FIG. 5.
Comparison of the bacterial total counts obtained with
the image analysis procedure ( ) and by manual counting ( ) for
three stations, two times of the year, and different depths.
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The number of examples needed to train a neural network depends very
much on the accuracy that is needed. For example, after
the network was
trained with just 4 examples of classes R and
V, it performed almost as
well as it did when it was trained with
60 examples (Fig.
2), but all
60 examples were needed to achieve
consistent levels of accuracy of
more than 90%. The network performed
best when examples of all classes
were used in roughly equal numbers
for training.
Bacterial concentrations.
As mentioned above, there was good
agreement between manual and machine counts for samples collected in
the summer months, but the presence of faint particles in samples
collected in the winter months resulted in disagreements (Fig. 5).
There was also a statistically significant increase in the fraction of
faint objects with depth. The nature of such faint objects is not
known. Perhaps they were dead cells with intact membranes
(29); it seems likely that they were bacterial in origin
considering their shape and size.
Blooms of bacteria belonging to the four morphological classes occurred
at all three stations, and the main peaks occurred
during the summer at
off-shore stations F9 and US5 and in the
autumn at coastal station NB1
(Fig.
6). Although not representing
strict taxonomic classes, small rods (class R1) medium rods (class
R2),
large rods (class R3), and crescent-shaped vibrios (class
V) were
distinguished. Most blooms peaked below the surface at
a depth of
8 m. Class R1 accounted for the greatest number of
bacteria. The
number of class R2 bacteria was about one-third
the number of class R1
bacteria, the number of class V bacteria
was roughly the same as the
number of class R2 bacteria, and there
were fewer class R3 bacteria. An
analysis of variance at the community
level, based on the averages for
five images determined by using
time and depth as factors (Table
1), confirmed the significance
of the
visually distinguishable patterns in Fig.
6, in which gray
scale
intervals correspond roughly to the precision expected with
95%
confidence.

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FIG. 6.
Concentrations of morphological classes of bacteria at
three stations in the Baltic Sea at different depths and times. Station
F9 is a subarctic off-shore site, station US5 is an off-shore site, and
station NB1 is a coastal site. Different shades correspond to
concentrations that could be discerned with 95% confidence. w, week.
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TABLE 1.
Analysis of variance of average bacterial concentrations
of members of four morphological classes at three stations with
time, with depth, and with time and depth
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Studies performed with molecular probes have resolved the bacteria into
about 10 to 20 dominant classes (
18). Therefore,
all of the
classes (R1, R2, R3, and V) were presumably composed
of several
different species that were not discernible on the
basis of morphology
alone. A two-dimensional histogram of biovolume
and
elongation for the whole survey showed that the objects formed
a
continuum for both biovolume and elongation (data not shown)
within the
resolution of the image analyzer, which was limited
by the digital
representations of objects as collections of pixels.
This indicated
that the categories based on elongation factors
(classes R1, R2, and
R3) corresponded to windows in a virtually
continuous elongation factor
spectrum. The biovolume histogram
within each window therefore
reflected the average dominating
biovolume within that window but
actually represented several
strains. Despite this problem, we made a
number of observations
which supported the theory that the bacterial
community was at
least partially resolved into subpopulations. (i) The
histograms
for each class in (Fig.
7)
showed that classes R1 and R2 each
displayed a Gaussian-shaped profile,
as expected for two distinct
populations. The profiles were truncated
slightly at smaller cell
sizes due to limitations in resolution. (ii)
The widths of the
class R1 and R2 histograms corresponded to roughly
twice their
modes (Fig.
7), which is consistent with the expectation
that
cells grow to approximately twice the average volume before they
divide. Accordingly, cells identified as being in the process
of
dividing had biovolumes in the upper range of the histograms
(Fig.
7).
Class R3 exhibited very similar characteristics. The
class V histogram
had a peak for the group containing the smallest
cells (0.023 µm
3). The relative sharpness of the class V peak is
consistent with
the smaller cell size, but the true nature of the small
cells
must be investigated at higher resolution.

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FIG. 7.
(R1, R2, R3, and V) Depth-integrated histograms for
classes R1, R2, R3, and V, respectively, at station US5 for week 32. (R1D, R2D, R3D, and VD) Dividing cell histograms for classes R1, R2,
R3, and V, respectively.
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Bacterial cell volumes.
A resolution of 0.12 µm per pixel
was chosen as a compromise between numbers of objects per image and
precision in feature rendering. However, the biovolume estimates
appeared to be quite precise. Measurements of fluorescent latex
microspheres revealed a high level of precision for volume estimates in
the bacterial size range (Table 2). The
standard deviations for measured values are related to the digital
sampling of the image formed by the optics. Volume is very sensitive to
inaccuracies in measurements. An inaccuracy of just 0.5 pixel in object
diameter results in a volume around the surface of the object which is
greater than both the standard deviation and the deviation from the
true value obtained when the edge detection procedure described above
is used.
Bacterial biovolume exhibited much less coherent patterns in space and
time than did bacterial abundance. This may have been
due in part to
insufficient sampling in time. The standard deviations
for measurements
at each sampling location and sampling time were
less than 12%. The
precision of the image analyzer should allow
discrimination of average
biovolumes from five images with an
accuracy of about 0.01 µm
3 with 95% confidence. The biovolume modes for class
R1 objects
fluctuated mainly between 0.04 and 0.07 µm
3.
Class R1 accounted for total biovolumes ranging from 1 × 10
8 ml/ml in the winter months to 10 × 10
8 ml/ml in the summer months. In comparison, the class
R2 biovolumes
ranged from 0.5 × 10
8 to 3 × 10
8 ml/ml while the class R3 and V biovolumes ranged from
0.1 × 10
8 and 1 × 10
8 ml/ml.
Sieracki and Viles (
21) performed a survey of bacteria
abundance and cell size in the North Atlantic Ocean along a
transect
by using image analysis. These authors noticed that the
particles
segregated into two main groups, as determined by
fluorescence
intensity and particle size. The average cell size for the
group
containing smaller particles was less than 0.04 µm
3, while the average cell size for the group containing
larger
cells was 0.11 µm
3. Sieracki and Viles assumed
that only the larger particles were
bacteria but did not rule out the
possibility that some of the
smaller particles could have been small
bacteria. A number of
other surveys of the Sargasso Sea and of Gulf
Stream and front
waters revealed average bacterial cell sizes
equivalent to those
found by us in this survey of the Baltic Sea
(
21).
The biovolumes derived from the image analysis for the off-shore
environments were similar to biovolumes reported by Häinenen
(
13) for the same area. The values for the coastal station,
however, were about one-half those reported by Andersson et al.
(
1). Häinenen used ocular grids in the microscopic
field to
determine bacterial size, while Andersson et al. used exposure
of diapositive photographs of microscopic fields digitized on
a graphic
tablet. The limited seasonal coverage of the two previous
studies
especially the study of Andersson et al., as well as differences
in the
methods used, may explain some of the differences between
the results
obtained.
Bacterial growth rates.
A number of objects classified as
dividing were examined to check the validity of the dividing cell
criterion (Fig. 4). The class R1 and R2 shapes included invaginations
and/or local maxima located symmetrically at each end of a cell, as
expected for cells undergoing division. This criterion appeared to be
less reliable for classes R3 and V, but this finding was not considered
to be very important since classes R1 and R2 accounted for the majority of the bacterial biomass and, presumably, biomass production. As a
separate check, the dividing cell biovolume histogram had modes
corresponding to roughly twice the average cell size for each class, as
expected (Fig. 7).
Class R1 was differentiated from class R2 on the basis of elongation
factors alone, but the same criterion did not logically
apply to the
corresponding dividing cells because of the much
more complex cell
shapes. It would have been theoretically possible
to plot the frequency
of dividing cells for each class, but elongation
factors alone did not
provide a strong enough criterion to identify
the classes of dividing
cells, so the frequencies were based on
both class R1 and class R2
data.
The FDC exhibited coherent patterns with time and depth, and the maxima
occurred during the summer months (Fig.
8). FDC ranging
from 1 to 5% were
consistent with the results of previous surveys
performed with samples
obtained from the Baltic Sea (
11,
12)
and are probably
typical of all pelagic communities. The FDC reflects
the growth rate of
a population. As a first approximation, septum-building
time
appears to be independent of growth rate at a constant temperature,
as
observed in growth experiments (
11,
12). Plotting FDC
against
growth rate at a constant temperature reveals an apparent
linear
relationship, but the slopes appear to vary with temperature and
lines often do not go through the origin as expected (i.e., FDC

0 when µ = 0). The consequences of these observations can be
partially explained by analyzing a simple model. Growth rate (µ)
is
dependent on the time that it takes a cell to grow to the point
where
it begins to divide (
tG) plus the time that it
actually
takes to divide (
tD):
|
(6)
|
The proportion of cells in the dividing phase relative to the
number of cells in the growing phase is the FDC:
|
(7)
|
If
tG from equation 7 is inserted into
equation 6, then:
|
(8)
|
The linear relationship is evident, and the slope can be
interpreted as the division (septum-building) time. Any line not
going
through the origin cannot be explained by this model and
might be
interpreted as the result of cells that have been arrested
in a
critical phase of the cell cycle and allowed to accumulate.
This can be
a particularly important problem in continuous culture
experiments that
lack predators which remove dead cells. In contrast
to the results of
many continuous-culture experiments, the FDC
values in this survey
decreased to less than 1% during the winter
(Fig.
8) which supports
this interpretation. An examination of
the relationships between FDC
values and growth rates from chemostat
experiments revealed that the
septum-building time (
tD) is approximately
1 h (
11,
12):
|
(9)
|
One problem with the FDC technique is that it depends on
identification of the actual fraction of live cells, which may be
quite
small under ordinary circumstances (
29). Special DAPI
(4',6-diamidino-2-phenylindole) staining techniques (
29) and
molecular techniques (
18) to identify the live fraction are
available. Another problem is that
tD probably
varies in different
species. Assuming that equation 9 reflects the
relationship between
the FDC and the growth rate under typical
conditions, the growth
rate varied between 0.005 h
1 in
the winter and 0.05 h
1 in the summer (Fig.
8).

View larger version (116K):
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|
FIG. 8.
Temperature, FDC based on data for classes R1 and R2
(see text), growth as calculated by using growth rate and concentration
(Fig. 6) assuming that 30% of the cells were actively growing, and
growth as estimated by thymidine incorporation (Thym. inc.) assays. w,
week.
|
|
The results obtained with the thymidine incorporation method
(
7,
8) reflect the number of cells that exhibit active
uptake of thymidine, whereas the FDC results reflect the growth
rate in
the growing fraction. The growth rates estimated by the
thymidine
incorporation method were comparable to the growth rates
calculated by
the FDC method if the fact that only a fraction
of the identifiable
cells were growing was taken into account.
However, the patterns of
growth with time obtained with the two
methods were different, which
left unanswered questions concerning
what aspects of growth each method
measures. For example, it is
known that calibrating thymidine
incorporation to growth rate
is not a simple procedure, as it has been
shown that thymidine
metabolism occurs under certain conditions
(
15). On the other
hand, the FDC procedure is labor
intensive, which has limited
its use. However, because of the new
technique described here,
extensive testing of the growth rate
relationship can be anticipated.
Other plankton classes.
High accuracy in edge detection was a
challenge for the image analyzer for cells as small as bacteria, but it
was less important for larger cells. The design of the
Laplace operator can be altered for analyzing such cells;
e.g., a larger convolution kernel can be used to reduce noise
sensitivity.
Even with shapes as simple as crescents (e.g., Class V), it is not easy
to find geometric parameters that can be used to achieve
the same
certainty of classification as the certainty achieved
with contour
descriptions. For more complex shapes, the number
of descriptors that
define a contour can be adjusted until features
of interest become
visible (Fig.
3). There are, of course, a limited
number of species
which can be identified by contour alone. More
complex network
architectures and description parameters can be
used, and remarkable
precision in classification can be achieved
(
5).
 |
ACKNOWLEDGMENTS |
We thank the European Commission (contract MAS2 - CT93- 0077) and
Umeå Marine Sciences Center (Umeå, Sweden) for financial support. We
thank other members of the DIADEME project, including Lars Kai Hansen
and Claus Svarer of the Technical University of Denmark, Bent Hygum of
Roskilde University (Roskilde, Denmark), Ramon Massana and Carlos
Pedrós-Alió of the Marine Science Institute of Spain, and
Jorma Kuparinen and Susanna Hietanen of the Finnish Institute of Marine
Research, for collaboration. We thank Umeå Marine Sciences Center for
access to equipment and the Swedish National Environmental Monitoring
Programme of the Baltic.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Marine
Biological Laboratory, Strandpromenaden 5, DK-3000 Helsingør, Denmark.
Phone: 45 49211633, ext. 326. Fax: 45 49261165. E-mail:
mblnb{at}mail.centrum.dk.
Present address: Kalmar University, S-39129 Kalmar, Sweden.
 |
REFERENCES |
| 1.
|
Andersson, A.,
U. Larsson, and Å. Hagström.
1986.
Size-selective grazing by a microflagellate on pelagic bacteria.
Mar. Ecol. Prog. Ser.
33:51-57.
|
| 2.
|
Bjørnsen, P. K., and J. Kuparinen.
1991.
Determination of bacterioplankton biomass, net production and growth efficiency in the southern ocean.
Mar. Ecol. Prog. Ser.
71:185-194.
|
| 3.
|
Bloem, J.,
M. Veninga, and J. Shepherd.
1995.
Fully automatic determination of soil bacterium numbers, cell volumes, and frequencies of dividing cells by confocal laser scanning microscopy and image analysis.
Appl. Environ. Microbiol.
61:926-936[Abstract].
|
| 4.
|
Culverhouse, P. F.,
R. Ellis,
R. G. Simpson,
R. Williams,
R. W. Pierce, and J. T. Turnver.
1994.
Automatic categorisation of five species of Cymatocyllis (Protozoa, Tintinnida) by artificial neural network.
Mar. Ecol. Prog. Ser.
107:272-280.
|
| 5.
|
Culverhouse, P. F.,
R. G. Simpson,
R. Ellis,
J. A. Lindley,
R. Williams,
T. Parisini,
B. Reguera,
I. Bravo,
R. Zoppoli,
G. Earnshaw,
H. McCall, and G. Smith.
1996.
Automatic classification of field-collected dinoflagellates by artificial neural network.
Mar. Ecol. Prog. Ser.
139:281-287.
|
| 6.
|
Frankel, D. S.,
R. J. Olson,
S. L. Frankel, and S. W. Chisholm.
1989.
Use of a neural net computer system for analysis of flow cytometric data of phytoplankton populations.
Cytometry
10:540-550[Medline].
|
| 7.
|
Fuhrman, J., and F. Azam.
1980.
Bacterioplankton secondary production estimates for coastal waters of British Columbia, Antarctica, and California.
Appl. Environ. Microbiol.
39:1085-1095[Abstract/Free Full Text].
|
| 8.
|
Fuhrman, J., and F. Azam.
1982.
Thymidine incorporation as a measure of heterotrophic bacterioplankton production in marine surface waters: evaluation and field results.
Mar. Biol.
66:109-120.
|
| 9.
|
Grover, N. B.,
C. L. Woldringh,
A. Zaritsky, and R. F. Rosenberger.
1977.
Elongation of rod-shaped bacteria.
J. Theor. Biol.
67:181-193[Medline].
|
| 10.
|
Haas, L. W.
1982.
Improved epifluorescence microscopy for observing planktonic micro-organisms.
Ann. Inst. Oceanogr.
58:261-266.
|
| 11.
|
Hagström, Å., and U. Larsson.
1984.
Diel and seasonal variation in growth rates of pelagic bacteria, p. 249-262.
In
J. E. Hobbie, and P. J. L. Williams (ed.), Heterotrophic activity in the sea. Plenum Publishing Corp., New York, N.Y.
|
| 12.
|
Hagström, Å.,
U. Larsson,
P. Hörstedt, and S. Normark.
1979.
Frequency of dividing cells, a new approach to the determination of bacterial growth rates in aquatic environments.
Appl. Environ. Microbiol.
37:805-812[Abstract/Free Full Text].
|
| 13.
|
Heinänen, A.
1992.
Bacterioplankton in the open Baltic Sea. Ph.D. thesis.
University of Helsinki, Helsinki, Finland.
|
| 14.
|
Hobbie, J. E.,
R. J. Daley, and S. Jasper.
1977.
Use of Nuclepore filters for counting bacteria by fluorescence microscopy.
Appl. Environ. Microbiol.
33:1225-1228[Abstract/Free Full Text].
|
| 15.
|
Hollibaugh, J. T.
1988.
Limitations of the [3H]thymidine method for estimating bacterial productivity due to thymidine metabolism.
Mar. Ecol. Prog. Ser.
43:19-30.
|
| 16.
|
Marr, D., and E. C. Hildreth.
1980.
Theory of edge detection.
Proc. R. Soc. Lond. B Biol. Sci.
207:187-217[Medline].
|
| 17.
|
Massana, R.,
J. M. Gasol,
P. K. Bjørnsen,
N. Blackburn,
Å. Hagström,
S. Heitanen,
B. H. Hygum,
J. Kuparinen, and C. Pedrós-Alió.
1997.
Measurements of bacterial size via image analysis of epi-fluorescence preparations: description of an inexpensive system and solutions to some of the most common problems.
Sci. Mar.
61:397-407.
|
| 18.
|
Pinhassi, J.,
U. L. Zweifel, and Å. Hagström.
1997.
Dominant marine bacterioplankton species found among colony-forming bacteria.
Appl. Environ. Microbiol.
63:3359-3366[Abstract].
|
| 19.
|
Porter, K. G., and Y. S. Feig.
1980.
The use of DAPI for identifying and counting aquatic microflora.
Limnol. Oceanogr.
25:943-948.
|
| 20.
|
Sieracki, M. E., and C. Viles.
1990.
Color image-analyzed fluorescence microscopy: a new tool for marine microbial ecology.
Oceanography
3:30-36.
|
| 21.
|
Sieracki, M. E., and C. L. Viles.
1992.
Distributions and fluorochrome-staining properties of sub-micrometer particles and bacteria in the North Atlantic.
Deep Sea Res.
39:1919-1929.
|
| 22.
|
Simpson, R.,
R. Williams,
R. Ellis, and P. F. Culverhouse.
1992.
Biological pattern recognition by neural networks.
Mar. Ecol. Prog. Ser.
79:303-308.
|
| 23.
|
Smith, D. C., and F. Azam.
1992.
A simple, economical method for measuring bacterial protein synthesis rates in seawater using 3H-leucine.
Mar. Microb. Foodwebs
6:107-114.
|
| 24.
|
Sokal, R. R., and F. J. Rohlf.
1995.
Biometry. W.H.
Freeman and Co., New York, N.Y.
|
| 25.
|
Stokseth, P. A.
1969.
Properties of a defocused optical system.
J. Optic. Soc. Am.
59:1314-1322.
|
| 26.
|
Svarer, C.
1994.
Neural networks for signal processing. Ph.D. thesis.
Technical University of Denmark, Lyngby, Denmark.
|
| 27.
|
Viles, C. L., and M. E. Sieracki.
1992.
Measurement of marine picoplankton cell size by using a cooled, charge-coupled device camera with image-analyzed fluorescence microscopy.
Appl. Environ. Microbiol.
58:584-592[Abstract/Free Full Text].
|
| 28.
|
Williams, S. C.,
P. G. Verity, and T. Beatty.
1995.
A new staining technique for dual identification of plankton and detritus in seawater.
J. Plankton Res.
17:2037-2047.
[Abstract/Free Full Text] |
| 29.
|
Zweifel, U. L., and Å. Hagström.
1995.
Total counts of marine bacteria include a large fraction of non-nucleoid-containing bacteria (ghosts).
Appl. Environ. Microbiol.
61:2180-2185[Abstract].
|
Applied and Environmental Microbiology, September 1998, p. 3246-3255, Vol. 64, No. 9
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Copyright © 1998, American Society for Microbiology. All rights reserved.
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